Battery Directive

Last updated

Rechargeable nickel-metal hydride AA batteries are among the types of batteries that the Battery Directive allows its general use. Four AA batteries.jpg
Rechargeable nickel–metal hydride AA batteries are among the types of batteries that the Battery Directive allows its general use.

The Directive 2006/66/EC of the European Parliament and of the Council of 6 September 2006 on batteries and accumulators and waste batteries and accumulators and repealing Directive 91/157/EEC, commonly known as the Battery Directive, regulates the manufacture and disposal of batteries in the European Union with the aim of "improving the environmental performance of batteries and accumulators". [1] :4 [2]

Contents

Batteries commonly contain hazardous elements such as mercury, cadmium, and lead, which when incinerated or landfilled, present a risk to the environment and human health.

Directive 91/157/EEC was adopted on 18 March 1991 to reduce these hazards by harmonising EU member states' laws on the disposal and recycling of batteries containing dangerous substances. [3] Directive 2006/66/EC repealed Directive 91/157/EEC and

Directive 2006/66/EC was amended by Directive 2013/56/EU of 20 November 2013, as regards the placing on the market of portable batteries and accumulators containing cadmium intended for use in cordless power tools, and of button cells with low mercury content, and repealing Commission Decision 2009/603/EC.

General

This directive, like many other European compliance directives, is not directly applicable, but requires legislative action from European Member States. Though European directives are legislation, European Union Member States must comply with them to avoid legal action that the European Commission can bring to bear if they don't. However Member States retain some freedom by what means they implement a directive's requirements.

The battery directive has the objective of improving the environmental performance of batteries by regulating the use of certain substances in the manufacture of batteries (lead, mercury, cadmium, etc.) and setting standards for the waste management of these batteries. [1] :4 Many European member states have passed battery and waste management laws. Among those nations are: Belgium, Sweden, Germany, Austria, Denmark, Finland, the United Kingdom, the Netherlands, France, and others. Finland and Denmark have supported a total prohibition of cadmium in batteries. Belgium and Sweden have battery recycling rates of 59% and 55% respectively. With the finalisation of the 2006 Battery Directive, European states now have specific guidelines to which to make rules to comport.

History

Early waste directives

The first of the western European directives dealing with waste management was the "Council Directive 75/442/EEC of 15 July 1975 on Waste." [4] It didn't mention batteries or chemicals but specified the regulation of "particular categories of waste," which was later referenced to by both Battery Directives as a legislative or legal basis. The first version of the European Council Directive on Batteries and Accumulators 91/157/EEC was approved on 18 March 1991. [5] It covered many battery types, including industrial, automotive, dry-cell, lead-acid, alkaline, nickel-cadmium, nickel-metal-hydride, lithium, lithium-ion, mercury, etc. The first program in the directive was set for a six-year duration, starting in 1993.

Provisions of the first directive

The 1991 battery Directive's "Article 3; MI; Annex I" stated the prohibition (with exceptions) of marketing:

  1. Batteries on the market after 18 September 1992 with:
    • 1.A. more than 25 mg of mercury per cell, except alkaline manganese batteries
    • 1.B. more than 0.025% cadmium by weight
    • 1.C. more than 0.4% lead by weight
  2. Alkaline manganese batteries placed on the market after 18 September 1992 containing more than 0.025% of mercury by weight
  3. Batteries on the market after 1 January 1999 with more than 0.0005% mercury by weight [6]


Since battery recycling rates then were about 5% the directive sought to improve these rates. It set up recycling goals: separate collection and recycling, and provide recycling/collection information to the consumer. The responsibility for providing separated recycling collection was largely given to the manufacturers. Recycling requirements are found in Articles 4, 6, and 7.

There were marking provisions, including manufacturer responsibility for marking on the battery products themselves the contained substances and recycling information.

Resistance

Regulation was met with heavy resistance. Disputed were deadlines, target recycling rates, implementation dates, weight percentage limits, applicable product groups, financial responsibility for public information campaigns and waste management (and its financial impact), exclusions of financial responsibility given to small producer businesses, and personnel safety from decreased reliability of "greener" batteries.

In a non-environmental battery marking question, automotive battery makers questioned markings on batteries relating to battery performance, arguing that the quantity of a car battery's electric current output to start a vehicle in extreme weather was a very good indicator of battery performance.

After poor implementation of the first Battery Directive, work began on a new directive that would more emphasise battery end-of-life waste management through mandated and better-structured collection and recycling programs. It was also acknowledged that more research on certain substance was needed before harsher, more complete, and, arguably, unrealistic, bans. Thus the onus was on everyone in the waste management chain, from producer to the consumer, rather than affecting product design with substance bans that manufacturers claimed are unreasonable.

Conciliation Committee's compromise

Consultations to revisions of the first battery Directive started in 1997, giving all interested parties a voice in legislation and policy, especially in assessing the directive's economic, environmental, and social impact. In February 2003 an open stakeholders consultation process was started, which published its findings online, and culminated in a meeting in Brussels, in July 2003. The waters were tested by asking for Extended Impact Assessments for different scenarios of proposed ranges of regulation. For example, what would be the impact in establishing spent battery collection targets of from 30% to 80% or the impact of SEPARATE spent battery collection of from 70% to 100%? Entities were asked how these goals could be met and to propose collection responsibility models.

The "green" viewpoint (and perhaps that of the Conciliation Committee's) [7] was that the previous Directive had been limited in scope, while groups on the other side set forth reasons for less stringency. Those arguing for broadening the scope claimed that if batteries with certain metals were not banned carte blanche then the waste management effort would be hurt by confusion and perhaps inconvenience to the public.

There were at least six drafts the 2003 version, which was equivalent to a second battery directive. The 2003 revision, Council Directive 2003/0282/COD, [8] a July 2006 "conciliation agreement," was a compromise between the European Council and European Parliament, and came after three years of draft revisions. It was welcomed by entities like the European Portable Battery Association (EPBA), that favoured less stringency. As in other models of European compliance legislation, a corporation or organisations like the EPBA participates in working groups with members that include, among other players, legislators, large enterprises—in this case, battery-makers—trade associations, and non-governmental organisations. The Directive's overall stated objective was still to protect the public interest with a cleaner environment by minimising the negative impact on the environment of batteries, especially in their waste cycle. Depending on the viewpoint, it was also something of a compromise between 1. manufacturers and distributors, and 3. environmental proponents.

2006 Battery Directive

The most recent Battery Directive, which entered into force on 26 September 2006, gave European Member States until 26 September 2008 to implement national laws and rules on batteries (Art.26 – Transposition). Some nations took the initiative and had already started programs and passed laws in accordance with the spirit and specifications of earlier battery directives.

With the exception of button cells with a mercury content of no more than 2% by weight, the 2006 Battery Directive restates the earlier Battery Directive's prohibition of marketing batteries with more than 0.0005% mercury and 0.002% cadmium by weight. However, some exceptions exist. The directive also mandates symbols for battery labels that indicate the battery's chemical contents if lead, mercury, or cadmium are used. According to this directive, lead content in batteries is no longer restricted.

There should be initiatives to reduce heavy metal in batteries, promote using less toxic substances in batteries, dispose of batteries properly (not via regular household waste, but properly separated), research initiatives in the above and in recycling. Consumers should be informed of the dangers in non-compliant disposal of old batteries. It also states that it must be easy for consumers to remove batteries from electronic products.

Battery disposal

Disposal of automotive and industrial batteries by leaving in landfills or by incineration "should be prohibited". (Directive preamble point #8)

Recycling and collection of batteries

Article 7 requires Member States to maximise the "separation" of batteries from regular municipal waste and requires spent batteries to be collected separately. Recycling and collection targets are called for so that fewer batteries end up in landfills.

The collection program is found in Annex I. It is proposed that member states set their own country's standards using the Battery Directive as a guide for minimum levels. These levels are stated in terms of percents of prior annual sales. Article 3(17) states "'collection rate' means, for a given Member State in a given calendar year, the percentage obtained by dividing the weight of waste portable batteries and accumulators collected in accordance with Article 8(1) of this Directive or with Directive 2002/96/EC in that calendar year by the average weight of portable batteries and accumulators that producers either sell directly to end-users or deliver to third parties in order to sell them to end-users in that Member State during that calendar year and the preceding two calendar years."

Member States are required to provide collection sites that are accessible and free of charge to the public (Art. 8). Battery distributors may be required to provide this at Member States' discretion (Art. 8(2)(a)). Battery manufacturers may not refuse to take back waste batteries from end-consumers, irrespective of their chemical composition or origin (Art. 8(3)).

Waste battery collection rate targets are specified in Article 10. Minimum targets of 25% of battery sales and 45% of battery sales by 26 September 2012 and 2016 respectively(Art. 10(2)).

Collections rates are to be monitored annually as outlined in Annex I scheme, with yearly reporting to the Commission. There may be some leeway given in the form of "transitional agreements" if a nation has special circumstances. (Art. 10 (4))

Exclusions and exemptions

There are many exclusions granted to manufacturers and certain product types. In some cases these are for batteries used in safety or other critical-use applications (e.g. miners' caps).

Exemptions for the following are still in place:

Inclusions

Batteries imported from third countries under non-discriminatory conditions are included (Art. 19).

Economic instruments

Member states may use instruments like differential tax rates to encourage less toxic batteries and recycling (Art. 9)

Implementation reports

Member states are required to submit implementation reports to the commission every three years (Art. 22).

Labelling

In Art. 21 marking must indicate separate collections or recycling and the heavy metal content. Labels should state collection information and chemical content of batteries. They should show a symbol of the "crossed-out" wheeled recycling bin (Annex II [10] ) to indicate that the battery should not go in the bin. This symbol size is specified as a percent of battery area on its largest side (3%), except for cylindrical batteries, where the symbol should be 1.5% of total surface area.

Penalties

Member states will set up measures for "effective, proportionate, and dissuasive" penalties for actions not comporting to the battery Directive and apprise the European Commission of these measures and any changes (Art. 25).

Collection targets

Annex I Battery Collection Targets mentioned in Art. 10 above:

Annex I – Monitoring of Compliance with the Article 10 Collection Targets
YearData collectionData collectionCalculationReporting Requirement
X*+1Sales in year 1 (S1)......
X+2Sales in year 2 (S2)......
X+3Sales in year 3 (S3)Collection in year 3 (C3)Collection rate (CR3) = 3*C3/(S1+S2+S3)..
X+4Sales in year 4 (S4)Collection in year 4 (C4)Collection rate (CR4) = 3*C4/(S2+S3+S4)

(Target set at 25%.)

..
X+5Sales in year 5 (S5)Collection in year 5 (C5)Collection rate (CR5) = 3*C5/(S3+S4+S5)CR4
X+6Sales in year 6 (S6)Collection in year 6 (C6)Collection rate (CR6) = 3*C6/(S4+S5+S6)CR5
X+7Sales in year 7 (S7)Collection in year 7 (C7)Collection rate (CR7) = 3*C7/(S5+S6+S7)CR6
X+8Sales in year 8 (S8)Collection in year 8 (C8)Collection rate (CR8) = 3*C8/(S6+S7+S8)

(Target set at 45%.)

CR7
X+9Sales in year 9 (S9)Collection in year 9 (C9)Collection rate (CR9) = 3*C9/(S7+S8+S9)CR8
X+10Sales in year 10 (S10)Collection in year 10 (C10)Collection rate (CR10) = 3*C10/(S8+S9+10)CR9
X+11Etc.Etc.Etc.CR10
Etc.........

In practice

In practice, manufacturers of batteries need to make sure they have applied the legal framework to their company. This means they need to check who the producer under legal terms of the directive is and whether they have fulfilled the labelling obligation. In the next step manufacturers or distributors have to define their battery strategy and register with battery compliance schemes to control battery compliance and monitor recycling and recovery results. [11] While working within the framework of the battery directive manufacturers, producers and distributors also have to be aware of financial aspects and registration timelines to ensure compliance and reduce risks of their batteries. Most of the time they are supported with advice by suitable qualified persons. [12]

The Mercury-Containing and Rechargeable Battery Management Act of 1996 is a similar law in the United States, banning the sale of mercury-containing batteries (except small button cells), and requiring labelling for disposal and recycling. The U.S. state of California and New York City require recycling of rechargeable batteries, and along with the state of Maine require the recycling of cell phones. [13]

Similar European pieces of legislation protecting the environment and health, parallel to the Battery Directive, are the Restriction of Hazardous Substances (RoHS), Waste Electrical and Electronic Equipment (WEEE) Directives and Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH) Regulation.

See also

Related Research Articles

<span class="mw-page-title-main">Nickel–cadmium battery</span> Type of rechargeable battery

The nickel–cadmium battery is a type of rechargeable battery using nickel oxide hydroxide and metallic cadmium as electrodes. The abbreviation Ni–Cd is derived from the chemical symbols of nickel (Ni) and cadmium (Cd): the abbreviation NiCad is a registered trademark of SAFT Corporation, although this brand name is commonly used to describe all Ni–Cd batteries.

<span class="mw-page-title-main">Waste Electrical and Electronic Equipment Directive</span> European Union recycling directive

The Waste Electrical and Electronic Equipment Directive is a European Community Directive, numbered 2012/19/EU, concerned with waste electrical and electronic equipment (WEEE). Together with the RoHS Directive 2011/65/EU, it became European Law in February 2003. The WEEE Directive set collection, recycling and recovery targets for all types of electrical goods, with a minimum rate of 4 kilograms (9 lb) per head of population per annum recovered for recycling by 2009. The RoHS Directive set restrictions upon European manufacturers as to the material content of new electronic equipment placed on the market.

<span class="mw-page-title-main">Restriction of Hazardous Substances Directive</span> European Union directive restricting ten hazardous materials

The Restriction of Hazardous Substances Directive 2002/95/EC, short for Directive on the restriction of the use of certain hazardous substances in electrical and electronic equipment, was adopted in February 2003 by the European Union.

<span class="mw-page-title-main">Alkaline battery</span> Type of electrical cell

An alkaline battery is a type of primary battery where the electrolyte has a pH value above 7. Typically these batteries derive energy from the reaction between zinc metal and manganese dioxide.

<span class="mw-page-title-main">Waste hierarchy</span> Tool to evaluate processes protecting the environment

Waste (management) hierarchy is a tool used in the evaluation of processes that protect the environment alongside resource and energy consumption from most favourable to least favourable actions. The hierarchy establishes preferred program priorities based on sustainability. To be sustainable, waste management cannot be solved only with technical end-of-pipe solutions and an integrated approach is necessary.

<span class="mw-page-title-main">Electronic waste recycling</span> Form of recycling

Electronic waste recycling, electronics recycling, or e-waste recycling is the disassembly and separation of components and raw materials of waste electronics; when referring to specific types of e-waste, the terms like computer recycling or mobile phone recycling may be used. Like other waste streams, reuse, donation, and repair are common sustainable ways to dispose of IT waste.

<span class="mw-page-title-main">Directive 67/548/EEC</span>

The Dangerous Substances Directive was one of the main European Union laws concerning chemical safety, until its full replacement by the new regulation CLP Regulation (2008), starting in 2016. It was made under Article 100 of the Treaty of Rome. By agreement, it is also applicable in the EEA, and compliance with the directive will ensure compliance with the relevant Swiss laws. The Directive ceased to be in force on 31 May 2015 and was repealed by Regulation (EC) No 1272/2008 of the European Parliament and of the Council of 16 December 2008 on classification, labelling and packaging of substances and mixtures, amending and repealing Directives 67/548/EEC and 1999/45/EC, and amending Regulation (EC) No 1907/2006.

<span class="mw-page-title-main">Mercury battery</span> Nonrechargeable battery cell

A mercury battery is a non-rechargeable electrochemical battery, a primary cell. Mercury batteries use a reaction between mercuric oxide and zinc electrodes in an alkaline electrolyte. The voltage during discharge remains practically constant at 1.35 volts, and the capacity is much greater than that of a similarly sized zinc-carbon battery. Mercury batteries were used in the shape of button cells for watches, hearing aids, cameras and calculators, and in larger forms for other applications.

<span class="mw-page-title-main">Electronic waste</span> Discarded electronic devices

Electronic waste describes discarded electrical or electronic devices. It is also commonly known as waste electrical and electronic equipment (WEEE) or end-of-life (EOL) electronics. Used electronics which are destined for refurbishment, reuse, resale, salvage recycling through material recovery, or disposal are also considered e-waste. Informal processing of e-waste in developing countries can lead to adverse human health effects and environmental pollution. The growing consumption of electronic goods due to the Digital Revolution and innovations in science and technology, such as bitcoin, has led to a global e-waste problem and hazard. The rapid exponential increase of e-waste is due to frequent new model releases and unnecessary purchases of electrical and electronic equipment (EEE), short innovation cycles and low recycling rates, and a drop in the average life span of computers.

<span class="mw-page-title-main">Button cell</span> Small battery

A button cell, watch battery, or coin battery is a small battery made of a single electrochemical cell and shaped as a squat cylinder typically 5 to 25 mm in diameter and 1 to 6 mm high – resembling a button. Stainless steel usually forms the bottom body and positive terminal of the cell; insulated from it, the metallic top cap forms the negative terminal.

<span class="mw-page-title-main">Landfills in the United Kingdom</span>

Landfills in the United Kingdom were historically the most commonly used option for waste disposal. Up until the 1980s, policies of successive governments had endorsed the "dilute and disperse" approach. Britain has since adopted the appropriate European legislation and landfill sites are generally operated as full containment facilities. However, many dilute and disperse sites remain throughout Britain.

<span class="mw-page-title-main">Landfill Directive</span> 1999 European Union directive

The Landfill Directive, more formally Council Directive 1999/31/EC of 26 April 1999, is a European Union directive which regulates waste management of landfills in the European Union. It was to be implemented by EU Member States by 16 July 2001. Directive (EU) 2018/850 amended the 1999 directive with effect from 5 July 2020.

<span class="mw-page-title-main">Battery recycling</span> Process

Battery recycling is a recycling activity that aims to reduce the number of batteries being disposed as municipal solid waste. Batteries contain a number of heavy metals and toxic chemicals and disposing of them by the same process as regular household waste has raised concerns over soil contamination and water pollution. While reducing the amount of pollutants being released through disposal through the uses of landfill and incineration, battery recycling can facilitate the release of harmful materials from batteries to both the environment and the workers recycling batteries.

The End of Life Vehicles Directive is a Directive of the European Union addressing the end of life for automotive products. Every year, motor vehicles which have reached the end of their useful lives create between 8 and 9 million tonnes of waste in the European Union. In 1997, the European Commission adopted a Proposal for a Directive to tackle this problem.

<span class="mw-page-title-main">Waste framework directive</span>

The Waste Framework Directive (WFD) is a European Union Directive concerned with "measures to protect the environment and human health by preventing or reducing the adverse impacts of the generation and management of waste and by reducing overall impacts of resource use and improving the efficiency of such use". The first Waste Framework Directive dates back to 1975. It had previously been substantially amended in 1991 and 2006. The present directive was adopted on 19 November 2008.

<span class="mw-page-title-main">Electronic waste by country</span>

Electronic waste is a significant part of today's global, post-consumer waste stream. Efforts are being made to recycle and reduce this waste.

<span class="mw-page-title-main">Waste management law</span> Area of law regarding waste

Waste management laws govern the transport, treatment, storage, and disposal of all manner of waste, including municipal solid waste, hazardous waste, and nuclear waste, among many other types. Waste laws are generally designed to minimize or eliminate the uncontrolled dispersal of waste materials into the environment in a manner that may cause ecological or biological harm, and include laws designed to reduce the generation of waste and promote or mandate waste recycling. Regulatory efforts include identifying and categorizing waste types and mandating transport, treatment, storage, and disposal practices.

Products made from a variety of materials can be recycled using a number of processes.

Technical Guidance WM2: Hazardous Waste: Interpretation of the definition and classification of hazardous waste is a guidance document developed and jointly published by the English Environment Agency, Natural Resources Wales, Scottish Environment Protection Agency and the Northern Ireland Environment Agency to provide guidance on the assessment and classification of hazardous waste based on the revised Waste Framework Directive definition of hazardous waste. Waste producers, consultants, contractors and waste management companies use the guidance to a) identify the correct waste code for their waste and b) determine whether the waste is hazardous or not based on its chemical composition.

References

  1. 1 2 3 4 5 6 7 8 9 "Directive 2006/66/EC of the European Parliament and of the Council of the 6 September 2006 on batteries and accumulators and repealing Directive 91/157/EEC" (PDF). Official Journal of the European Union (L 266). European Union. 26 September 2006. Retrieved 13 November 2015.
  2. European Commission webpage on Batteries "Environment - Title". Archived from the original on 13 January 2009. Retrieved 9 January 2009.. Retrieved 19 October 2010
  3. Council Directive 91/157/EEC of 18 March 1991 on batteries and accumulators containing certain dangerous substances Article 1. Retrieved 18 October 2010
  4. Council Directive 75/442/EEC of 15 July 1975 on Waste European Union Website. Retrieved 15.11.06
  5. "Council Directive of 18 March 1991 on Batteries and Accumulators Containing Certain Dangerous Substances" (PDF). European Union. 25 January 1999. Archived from the original (PDF) on 7 May 2006. Retrieved 6 November 2015.
    1. Batteries on the market after 18 September 1992 with:
      • 1.A. more than 25 mg of mercury per cell, except alkaline manganese batteries
      • 1.B. more than 0.025% cadmium by weight
      • 1.C. more than 0.4% lead by weight
    2. Alkaline manganese batteries placed on the market after 18 September 1992 containing more than 0.025% of mercury by weight
    3. Batteries on the market after 1 January 1999 with more than 0.0005% mercury by weight
  6. Consultation Document on the Revision of the Battery Directive Archived 19 May 2011 at the Wayback Machine European Union Website. Retrieved 15.11.06
  7. 2003 Council Directive 2003/0282/COD Revision Archived 24 September 2006 at the Wayback Machine European Union Website. Retrieved 15.11.06
  8. On 26 March 2012, the Commission adopted a proposal for a Directive ending the exemption for cordless power tools 1 January 2016.
  9. Annex II Archived 27 September 2007 at the Wayback Machine BMU Website. Retrieved 15.11.06
  10. "Batteries Directive – Environment Agency". environment-agency.gov.uk. Archived from the original on 16 January 2013. Retrieved 25 April 2018.
  11. "Rolex Datejust II Ref.116334 – seltene 41mm Herrenuhr mit geriffelter 18K weißgold Lünette – Ich liebe Uhren" (PDF). 1weee-services.com. Retrieved 25 April 2018.[ permanent dead link ]
  12. "Rechargeable Battery Recycling Corporation". Archived from the original on 31 January 2009. Retrieved 9 January 2009.